US6159373A - Cleaning of hollow fibre membranes - Google Patents
Cleaning of hollow fibre membranes Download PDFInfo
- Publication number
- US6159373A US6159373A US08/809,679 US80967997A US6159373A US 6159373 A US6159373 A US 6159373A US 80967997 A US80967997 A US 80967997A US 6159373 A US6159373 A US 6159373A
- Authority
- US
- United States
- Prior art keywords
- lumens
- fibres
- shell
- walls
- backwash
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
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Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D65/00—Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
- B01D65/02—Membrane cleaning or sterilisation ; Membrane regeneration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D29/00—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor
- B01D29/11—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor with bag, cage, hose, tube, sleeve or like filtering elements
- B01D29/114—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor with bag, cage, hose, tube, sleeve or like filtering elements arranged for inward flow filtration
- B01D29/115—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor with bag, cage, hose, tube, sleeve or like filtering elements arranged for inward flow filtration open-ended, the arrival of the mixture to be filtered and the discharge of the concentrated mixture are situated on both opposite sides of the filtering element
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D29/00—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor
- B01D29/50—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor with multiple filtering elements, characterised by their mutual disposition
- B01D29/52—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor with multiple filtering elements, characterised by their mutual disposition in parallel connection
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D29/00—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor
- B01D29/62—Regenerating the filter material in the filter
- B01D29/64—Regenerating the filter material in the filter by scrapers, brushes, nozzles, or the like, acting on the cake side of the filtering element
- B01D29/6438—Regenerating the filter material in the filter by scrapers, brushes, nozzles, or the like, acting on the cake side of the filtering element nozzles
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D29/00—Filters with filtering elements stationary during filtration, e.g. pressure or suction filters, not covered by groups B01D24/00 - B01D27/00; Filtering elements therefor
- B01D29/62—Regenerating the filter material in the filter
- B01D29/66—Regenerating the filter material in the filter by flushing, e.g. counter-current air-bumps
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/14—Ultrafiltration; Microfiltration
- B01D61/20—Accessories; Auxiliary operations
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D63/00—Apparatus in general for separation processes using semi-permeable membranes
- B01D63/02—Hollow fibre modules
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
- B01D2321/04—Backflushing
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
- B01D2321/18—Use of gases
- B01D2321/185—Aeration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
- B01D2321/20—By influencing the flow
- B01D2321/2066—Pulsated flow
Definitions
- the present invention relates to concentration of solids in a suspension using a hollow fibre membrane and, in particular forms, to methods and apparatus for periodically cleaning by backwashing the hollow fibre membranes.
- transmembrane pressure differential necessary to effect concentration of the solids in the prior art is achieved by pressurising the feedstock which necessitates the use of pumps, other ancillary equipment and, of course, a closed filter cartridge.
- Backwashing of such prior art concentrators involves increasing the pressure on both sides of the hollow fibres within the closed shell to a relatively high value before suddenly releasing that pressure on the shell side of the fibre walls to effect a sudden pressure differential across the walls which causes a backwash action.
- the present invention in at least some embodiments, provides a method of backwashing a hollow fibre filter which retains some of the features of the prior art, but optimizes a number of these features to provide improved performance.
- the time lapse between the start of an increase in negative transmembrane pressure (TMP) and such TMP reaching a maximum value corresponding to the explosive decompression is in the range of about 0.05 seconds to about 5 seconds.
- the fibres are rewetted prior to recommencing the filtration operation.
- feed liquid is pumped into the shell side of the filter while fluid pressure is still being applied to said lumens.
- fluid pressure is still being applied to said lumens.
- the fluid pressure during this phase preferably should exceed the shell side pressure by about 10 kPa to about 800 kPa.
- the steps of the method are carried out as a continuous process utilizing repetitive cycles of solids retention and backwash.
- step (b) is effected by allowing said remaining filtrate to drain out of said lumens of its own volition.
- the present invention provides a concentrator for recovering fine solids from a liquid feed suspension and having an operating cycle including a concentration part of the cycle in which solids present in the feed suspension are concentrated and a backwash part of the cycle in which supply of feed suspension to the concentrator is interrupted, said concentrator comprising:
- (v) means for terminating the concentration part of the cycle by ceasing supply of feed to said exterior surface of said fibres
- (viii) means for applying a source of fluid under pressure to said lumens before, at the same time as, or just after opening the shell to atmosphere, to cause explosive decompression through the walls of the fibres whereby said fluid under pressure passes through said walls;
- (ix) means for maintaining the pressure level in said lumens at a predetermined value for a sufficient time following said decompression to cause substantial portions of solids lodged within and/or on said fibre walls to be dislodged;
- (x) means for washing dislodged contaminant matter away by the application of a flow of liquid over the external surface of said fibre walls;
- (xi) means for recommencing the concentration part of the operating cycle by introducing said supply of feed suspension to said exterior surface of said fibres.
- the concentrator includes means for rewetting the fibres before recommencing concentration.
- fluid pressure is applied to remove the filtrate from the lumens
- this pressure is typically in the range of about 10 to about 600 kPa.
- the fluid pressure applied to the lumens prior to the decompression is typically in the range of about 100 to about 1200 kPa.
- Prior art hollow-fibre type ultrafilters are usually fed from the inside of the fibres for many well known reasons.
- feedstock is applied to the outside of the fibres and gas is introduced into the lumen of the fibre as the back-wash medium.
- the lumen pressure swells a suitably designed fibre so that the pores are enlarged whereby the particles are freed and swept away in the expansion of the back-wash gas.
- the fibres are made from thermoplastic polymers such as:
- gas as a back-wash medium enables the removal of fouling species by explosive decompression of the gas through the membrane structure for the minor part and at the outer membrane surface for the major part.
- the gaseous back-wash step is carried out at a pressure which is sufficient to overcome the effect of the surface tension of the continuous phase of the feedstock within the pores of the membrane.
- the gas backwashing phase should be limited to below 5 seconds to avoid drying out of the fibres and thus difficulty in recommencing filtration due to gas bubble retention in the fibre pores.
- the introduction of improved rewetting techniques has overcome this problem and it has been discovered that extending the gas backwash phase beyond 5 seconds has significant advantages. Time periods of up to 60 seconds have been found to be effective. A longer backwash provides improved removal of trapped solids. Also, where liquid is reintroduced to the shell prior to completion of the gas backwash, it has enabled the overlap where gas and liquid are both present to be extended. An overlap time of about 1 to about 30 seconds is preferable. This is desirable in large arrays where it may take considerable time, with normal pump pressures, to refill the shells with liquid. The extended time period enables normal pumps to be used to achieve the above overlap while it also avoids maldistribution of pressure within large filter arrays by allowing relatively slow refilling of the filter shells.
- the high pressure fluid application to the lumens may be pulsed to provide a number of explosive decompressions within the backwashing phase. These individual pulses are preferably between about 0.1 seconds and about 5 seconds in duration. This provides an advantage of reducing gas consumption in the backwash phase.
- the pulsing may be achieved by sealing and opening the shell at appropriate time intervals sufficient to allow pressure within the lumens to build up to a required level.
- the pressure supply may be pulsed to achieve the same effect.
- the pressure may be varied between a high and low level without actual total shut off of pressure.
- FIG. 1 shows a schematic representation of a hollow fibre cross-flow concentrator to which the present invention is applicable in an operating mode
- FIG. 2 shows the concentrator of FIG. 1 in backwash mode
- FIG. 3 shows a graph of transmembrane pressure (TMP) versus time for a standard backwash
- FIG. 4 shows a similar graph to FIG. 3 using a backwash according to one aspect of the invention
- FIG. 5 shows a normalized flow/TMP versus time graph for a standard backwash
- FIG. 6 shows a normalized flow/TMP versus time graph for the same type of machine as FIG. 5 but using the backwash according to one aspect of the invention
- FIG. 7 shows a graph of TMP versus time for a backwash where feed liquid is pumped into the filter while the gas backwash is still applied;
- FIG. 8 shows a normalized flow/TMP versus time graph for a standard backwash
- FIG. 9 shows a normalized flow/TMP versus time graph for the same type of machine as FIG. 8 but introducing feed liquid during the backwash cycle;
- FIG. 10 shows a normalized flow/TMP versus time graph for a standard backwash at a further installation
- FIG. 11 shows a normalized flow/TMP versus time graph for the same type of machine as FIG. 10 but introducing feed liquid during the backwash cycle.
- the hollow fibre cross-flow concentrator 10 shown in FIGS. 1 and 2 includes a cartridge shell 11 within which is positioned a bundle of hollow, porous, polymeric fibres 12.
- each fibre is made of polypropylene, has an average pore size of 0.2 ⁇ m, an internal lumen diameter in the range 250 ⁇ m to 310 ⁇ m and a fibre diameter in the range 500 ⁇ m to 650 ⁇ m.
- Polyurethane potting compound 13,14 holds the ends of the fibres 12 in place without blocking their lumens and closes off each end of the shell 11.
- the liquid feed suspension to be concentrated is pumped into the shell 11 through feed suspension inlet 15 and passes over the external walls of the hollow fibres 12. Some of the feed suspension passes through the walls of the fibres 12 into the lumens of the fibres to be drawn off through the lumen outlet port 16 as clarified liquid.
- the remaining feed suspension and some of the rejected species flows between the fibres 12 and leaves the shell 11 through outlet 17.
- the remainder of the rejected species is held onto or within the fibres or is otherwise retained within the shell.
- Lumen inlet port 18 remains closed during the operating mode of the concentrator shown in FIG. 1.
- lumen outlet port 16 is closed so that the flow of clarified liquid is stopped.
- the clarified liquid is then removed from the lumens by natural drainage or by introducing a pressurized gas through lumen inlet port 18 to force the liquid from the lumens.
- high pressure compressed gas is introduced through inlet 18 and the lumens of the fibres 12.
- the liquid-filled shell is sealed and gas cannot penetrate the porous walls even though the gas pressure is now raised well above the normal bubble point of the fibre walls because the liquid within the shell is relatively incompressible. A reservoir of high pressure gas is thus accumulated in the fibre lumens.
- the shell outlet 17 is then opened which allows gas to penetrate the pores along the whole length of each fibre. This results in a explosive decompression of the pressurized gas through the walls of the fibres resulting in the retained solids in the fibre walls being dislodged from the fibres into the feed side of the filter.
- the initial breakthrough of gas through the fibre wall results in a tendency for pressure to drop in the lumens. It is desirable if this pressure can be maintained for a short period following decompression to cause increased flow through the fibre wall and greater removal of retained solids. This is preferably achieved by providing a large diameter pressure feed to the lumens and/or a higher pressure to compensate for pressure drop. In some cases, it is desirable to admit gas through both lumen ports 16 and 18 after carrying out the above described pressurised, trapped gas operation.
- the shell is opened just before or at the same time as the pressurized gas is applied to the lumens.
- An M10C (250 ⁇ m lumen) filter unit was run using a larger airline to provide an increased and prolonged pressure to the lumens following the explosive decompression phase.
- a 2.5 cm airline was used instead of a standard 10 mm airline.
- TMP negative transmembrane pressure
- the air consumption was higher than that for a standard backwash.
- the pressure profiles of the two different backwashes are shown in FIGS. 3 and 4.
- the TMP rise is significantly reduced when the "mega" backwash is used.
- the TMP rise per day for the ⁇ mega ⁇ backwash was approximately one quarter of the TMP rise seen with the standard backwash. This result means that machines could be run for longer between cleaning cycles, or the machines could give a higher throughput for the same cleaning interval.
- This example relates to the procedure where feed liquid is reintroduced to shell while the gas backwash is still proceeding.
- a trial was carried out on surface water to compare a standard backwash with a backwash stage using pressurized gas plus feed liquid. This stage is typically referred to as an "air on pump on” stage (AOPO stage).
- AOPO stage air on pump on stage
- FIGS. 8 and 10 illustrate the results of two consecutive runs of a filter unit and show that the TMP, when the standard backwash was used, rose to 400 kPa within 4 days of operation. At this point the unit could no longer maintain the set flow of 200 L/hr/em.
- FIGS. 9 and 11 show that when the AOPO stage was used the TMP remained below 150 kPa for 7 days. The result of this is that the filter units could maintain a higher flow rate for a longer period of time when the AOPO stage is used in the backwash. This is important to filter unit efficiency as the units require chemical cleaning when the TMP reaches a predetermined value.
- the decompression stage consists of the lumens being pressurized to 600 kPa, then the shell side valves being released whilst still supplying air to the lumens (for typically 1 to 3 seconds on most applications).
- the AOPO stage would extend the amount of time air is resupplied to the fibre lumens by typically an extra 1 to 30 seconds on M10 units.
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- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Engineering & Computer Science (AREA)
- Water Supply & Treatment (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Spinning Methods And Devices For Manufacturing Artificial Fibers (AREA)
- Artificial Filaments (AREA)
- External Artificial Organs (AREA)
Abstract
Description
TABLE 1
______________________________________
M10C (250 μm lumens) comparison of `mega` and
standard backwashes
BACKWASH
TYPE STANDARD MEGA
______________________________________
Module Type
PP M10C (20,000 fibres)
PP M10C (20,000 fibres)
Feed Type River water River water
Feed Turbidity 8 7
(NTU)
Feed Temperature 9.3 9.3
(° C.)
TMP (kPa) 103 92
TMP Range (kPa) 82 to 108 86 to 91
Instantaneous Flow* 2084 2223
(L/hr/module)
Instantaneous Flow* 2855 3045
(L/hr/module) at
20° C.
______________________________________
*Instantaneous flow is the average of instantaneous flowrates measured.
Claims (9)
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AUPM8006 | 1994-09-09 | ||
| AUPM8006A AUPM800694A0 (en) | 1994-09-09 | 1994-09-09 | Cleaning of hollow fibre membranes |
| PCT/AU1995/000587 WO1996007470A1 (en) | 1994-09-09 | 1995-09-08 | Cleaning of hollow fibre membranes |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| US6159373A true US6159373A (en) | 2000-12-12 |
Family
ID=3782526
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US08/809,679 Expired - Lifetime US6159373A (en) | 1994-09-09 | 1995-09-08 | Cleaning of hollow fibre membranes |
Country Status (11)
| Country | Link |
|---|---|
| US (1) | US6159373A (en) |
| EP (1) | EP0779835B1 (en) |
| JP (1) | JP3704544B2 (en) |
| KR (1) | KR100385044B1 (en) |
| CN (1) | CN1071588C (en) |
| AT (1) | ATE253973T1 (en) |
| AU (2) | AUPM800694A0 (en) |
| CA (1) | CA2199356C (en) |
| DE (1) | DE69532129T2 (en) |
| ES (1) | ES2207654T3 (en) |
| WO (1) | WO1996007470A1 (en) |
Cited By (58)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6524481B2 (en) | 1998-09-25 | 2003-02-25 | U.S. Filter Wastewater Group, Inc. | Apparatus and method for cleaning membrane filtration modules |
| US20030150807A1 (en) * | 2002-01-09 | 2003-08-14 | Hydranautics | Methods for improving filtration performance of hollow fiber membranes |
| WO2004056458A2 (en) | 2002-12-19 | 2004-07-08 | Hydranautics | Methods for cleaning and maintaining membrane surface during filtration |
| US6783008B2 (en) | 2000-04-10 | 2004-08-31 | U.S. Filter Wastewater Group, Inc. | Hollow fibre restraining system |
| US20040188339A1 (en) * | 2003-03-05 | 2004-09-30 | Hydranautics | Submergible membrane modular filtration device having replaceable membrane elements |
| US6821420B2 (en) | 1998-09-25 | 2004-11-23 | U. S. Filter Wastewater Group, Inc. | Apparatus and method for cleaning membrane filtration modules |
| US6872305B2 (en) | 2000-10-09 | 2005-03-29 | U.S. Filter Wastewater Group, Inc. | Membrane filtration system |
| US6884350B2 (en) | 2000-11-13 | 2005-04-26 | U.S. Filter Wastewater Group, Inc. | Modified membranes |
| US6955762B2 (en) | 2001-11-16 | 2005-10-18 | U. S. Filter Wastewater Group, Inc. | Method of cleaning membranes |
| US6974554B2 (en) | 2001-04-04 | 2005-12-13 | U.S. Filter Wastewater Group, Inc. | Potting method |
| US7018533B2 (en) | 2001-09-18 | 2006-03-28 | U.S. Filter Wastewater Group, Inc. | High solids module |
| US20060266705A1 (en) * | 2005-04-22 | 2006-11-30 | Arnold Janson | Refreshing chemicals during membrane cleaning |
| US7226541B2 (en) | 2001-06-20 | 2007-06-05 | Siemens Water Technology Corp. | Membrane polymer compositions |
| US7247238B2 (en) | 2002-02-12 | 2007-07-24 | Siemens Water Technologies Corp. | Poly(ethylene chlorotrifluoroethylene) membranes |
| US7264716B2 (en) | 1999-04-20 | 2007-09-04 | Siemens Water Technologies Corp. | Membrane filtration manifold system |
| AU2002322160B2 (en) * | 2001-08-09 | 2008-05-01 | Evoqua Water Technologies Llc | Method of cleaning membrane modules |
| US7387723B2 (en) | 2004-04-22 | 2008-06-17 | Siemens Water Technologies Corp. | Filtration apparatus comprising a membrane bioreactor and a treatment vessel for digesting organic materials |
| US7455765B2 (en) | 2006-01-25 | 2008-11-25 | Siemens Water Technologies Corp. | Wastewater treatment system and method |
| US7563363B2 (en) | 2005-10-05 | 2009-07-21 | Siemens Water Technologies Corp. | System for treating wastewater |
| US7591950B2 (en) | 2004-11-02 | 2009-09-22 | Siemens Water Technologies Corp. | Submerged cross-flow filtration |
| US7718057B2 (en) | 2005-10-05 | 2010-05-18 | Siemens Water Technologies Corp. | Wastewater treatment system |
| US7819956B2 (en) | 2004-07-02 | 2010-10-26 | Siemens Water Technologies Corp. | Gas transfer membrane |
| US7862719B2 (en) | 2004-08-20 | 2011-01-04 | Siemens Water Technologies Corp. | Square membrane manifold system |
| US7867417B2 (en) | 2004-12-03 | 2011-01-11 | Siemens Water Technologies Corp. | Membrane post treatment |
| US20110067737A1 (en) * | 2008-05-30 | 2011-03-24 | Beijing Ecojoy Water Technology Co., Ltd. | Method and apparatus for cleaning a film seperating device |
| US7938966B2 (en) | 2002-10-10 | 2011-05-10 | Siemens Water Technologies Corp. | Backwash method |
| US8048306B2 (en) | 1996-12-20 | 2011-11-01 | Siemens Industry, Inc. | Scouring method |
| US8057574B2 (en) | 2003-07-08 | 2011-11-15 | Siemens Industry, Inc. | Membrane post treatment |
| US8182687B2 (en) | 2002-06-18 | 2012-05-22 | Siemens Industry, Inc. | Methods of minimising the effect of integrity loss in hollow fibre membrane modules |
| US8268176B2 (en) | 2003-08-29 | 2012-09-18 | Siemens Industry, Inc. | Backwash |
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| GB9621339D0 (en) * | 1996-10-12 | 1996-12-04 | United Utilities Plc | Filter |
| AUPO377796A0 (en) * | 1996-11-21 | 1996-12-19 | Memtec America Corporation | Microporous membrane filtration and backwashing process |
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Also Published As
| Publication number | Publication date |
|---|---|
| DE69532129T2 (en) | 2004-04-15 |
| EP0779835A1 (en) | 1997-06-25 |
| EP0779835A4 (en) | 1998-12-02 |
| KR970705431A (en) | 1997-10-09 |
| ES2207654T3 (en) | 2004-06-01 |
| CA2199356A1 (en) | 1996-03-14 |
| CN1071588C (en) | 2001-09-26 |
| AU3466195A (en) | 1996-03-27 |
| JP3704544B2 (en) | 2005-10-12 |
| WO1996007470A1 (en) | 1996-03-14 |
| ATE253973T1 (en) | 2003-11-15 |
| JPH10504996A (en) | 1998-05-19 |
| AU686879B2 (en) | 1998-02-12 |
| AUPM800694A0 (en) | 1994-10-06 |
| DE69532129D1 (en) | 2003-12-18 |
| EP0779835B1 (en) | 2003-11-12 |
| CN1159769A (en) | 1997-09-17 |
| CA2199356C (en) | 2006-11-07 |
| KR100385044B1 (en) | 2003-08-19 |
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